Method for removal of metal atoms from aqueous solution using suspended plant cells

ABSTRACT

The use of plant suspension cultures to remove ionic metallic species and TNT-based explosives and their oxidation products from aqueous solution is described. Several plant strains were investigated including D. innoxia, Citrus citrus, and Black Mexican Sweet Corn. All showed significant ability to remove metal ions. Ions removed to sub-ppm levels include barium, iron, and plutonium. D. innoxia cells growing in media containing weapons effluent contaminated with Ba 2+   also remove TNT, other explosives and oxidation products thereof from solution. The use of dead, dehydrated cells were also found to be of use in treating waste directly.

BACKGROUND OF THE INVENTION

The present invention relates generally to water purification, and more particularly to the use of plant cells in suspension to remove metal atoms and explosives from aqueous solution. This invention is the result of Contract No. W-7405-ENG-36 between the Regents of the University of California and the U.S. Department of Energy.

Barium ion (Ba²⁺) has been used extensively in the production of conventional explosives in the explosive formulation Baratol, a 2,4,6-trinitrotoluene-based (TNT-based) castable mixture which consists of 76% (w/w) barium nitrate ground to a specific particle size and 24% TNT. Explosives are routinely machined underwater, resulting in the contamination of the aqueous solution with Ba²⁺ and TNT.

Four families of high-temperature superconducting ceramic oxides are currently being investigated. Three of these families contain significant amounts of Ba²⁺. The environmental impact of the production of such materials on a large scale will likely include the production of effluent containing high concentrations of barium and other toxic metal ions.

Barium is toxic to humans and to other species and must be removed prior to environmental discharge of effluents from production facilities. Environmental Protection Agency standards presently require the removal of this ion to concentrations below 100 ppm. New guidelines may require that substantially less Ba²⁺ can be released. Current methods for barium removal include the conversion of barium nitrate into less soluble barium sulfate which can be precipitated from effluent waters prior to their release. The resulting precipitate is subsequently buried. The overall process is relatively expensive and some barium is still released into the environment.

TNT, oxidation products thereof, and other soluble explosive materials are also found in these effluent waters. Most of these compounds are similarly toxic and must be reduced to environmentally acceptable levels before the water may be released. Current technology requires the step-wise removal of Ba²⁺ followed by the removal of these explosive compounds with activated charcoal and incineration of the charcoal. A simpler, more efficient process, and one which also removes other toxic materials from the effluent, is needed for the processing of large amounts of effluent prior to environmental discharge.

Remediation of water-borne plutonium and other actinide elements is a likewise well-known problem for the nuclear power industry and for the nuclear weapons complex. Simple, inexpensive, and efficient removal procedures are actively being sought to enable these industries to comply with increasingly stringent environmental regulations and with public concerns.

Plant cell suspension cultures can be selected for growth in concentrations of certain metal ions which are toxic to many other species. Survival may result from the production of small, metal-binding polypeptides which tightly bind all of the toxic ions entering the cells. See, e.g., P. J. Jackson, C. J. Unkefer, J. A. Watt, and N. J. Robinson, "Poly(γ-glutamylcysteinyl)glycine: Its Role In Cadmium Resistance In Plant Cells," Proc. Natl. Acad. Sci. USA 84, 6619 (1987). Alternatively, tolerance may be associated with the ability to exclude the metal ions from the cells. See, e.g., C. D. Foy, R. L. Chaney, and M. C. White, "The Physiology Of Metal Toxicity In Plants," Annu. Rev. Plant Physiol. 29, 511 (1978). The latter reference describes the uptake of metals by whole plants and suggests a role of whole plants in environmental cleanup and stabilization of contaminated sites, but no parallel action has been observed or predicted for plant cell cultures. Certain plants are already being used to stabilize sites contaminated with toxic trace metal ions (See, e.g., R. R. Gemmel, "Colonization of Industrial Wasteland" (Arnold Publishing Company, London, 1977)).

Fletcher et al. have demonstrated in "Metabolism of 2-chlorobiphenyl by Suspension Cultures of Paul's Scarlet Rose," by J. S. Fletcher, A. W. Groeger, and J. C. McFarlane, Bull. Environ. Contam. Toxicol. 39, 960 (1987) that suspension cultures of Rose remove PCBs from solution and chemically modify them.

Accordingly, it is an object of the present invention to substantially reduce the concentration of chosen metal ions from aqueous solution.

Another object of my invention is to substantially reduce the concentration of TNT in aqueous solution.

Yet another object of the invention is to substantially reduce the concentration of other explosives and explosive oxidation products in aqueous solution.

Additional objects, advantages, and novel features of the invention will be set forth in part in the description which follows, and in part will become apparent to those skilled in the art upon examination of the following or may be learned by practice of the invention. The objects and advantages of the invention may be realized and attained by means of the instrumentalities and combinations particularly pointed out in the appended claims.

SUMMARY OF THE INVENTION

To achieve the foregoing and other objects, and in accordance with the purposes of the present invention, as embodied and broadly described herein, the method hereof may include mixing an aqueous solution of a target metal ion and/or explosives to be removed therefrom with a suspension of plant cells, and separating the plant cells from the liquid after a sufficient interaction time has occurred. Preferably, the plant cells comprise Datura innoxia (D. innoxia). It is also preferred that the plant cells have been selected for growth in concentrations of the target metal ion and/or explosive.

Benefits and advantages of the present invention include efficient and economical removal of toxic and radioactive metals and harmful explosives and their oxidation products from aqueous solution using abundant, readily generated, and available plant cells.

BRIEF DESCRIPTION OF THE DRAWINGS

The accompanying drawings, which are incorporated in and form a part of the specification, illustrate an embodiment of the present invention and, together with the description, serve to explain the principles of the invention. In the drawings:

FIG. 1 graphically illustrates the growth of D. innoxia cells in aqueous suspensions containing concentrations of Ba²⁺ ranging from 0 to 1000 μM of Ba(NO₃)₂. Close overlap of the curves prevents detailed identification and separation of the five concentrations investigated.

FIG. 2 graphically illustrates the removal of Ba²⁺ from aqueous solution by rapidly growing D. innoxia cell suspension cultures grown in media containing different initial concentrations of Ba(NO₃)₂.

FIG. 3 graphically illustrates the rate of uptake of Ba²⁺ with time by D. innoxia cells.

FIG. 4 graphically illustrates the stability of metal-binding of extracts of D. innoxia cells in solutions containing different H⁺ concentrations.

FIG. 5 graphically illustrates the binding of Ba²⁺ by extracts of D. innoxia in solutions containing different Na⁺ concentrations.

FIG. 6 graphically illustrates the removal of explosive compounds by D. innoxia cells.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS OF THE INVENTION

Briefly, the present invention includes the use of plant suspension cultures to remove ionic metallic species and TNT-based explosives and their oxidation products from aqueous solution. Several plant strains were investigated including D. innoxia, Citrus citrus, and Black Mexican Sweet Corn (BMS). All showed significant ability to remove metal ions. Ions removed to sub-ppm levels include barium, iron, and plutonium. D. innoxia cells growing in media containing weapons effluent contaminated with Ba²⁺ also remove TNT, other explosives, and oxidation products thereof from solution. The technology to grow plant cell suspension cultures in fermenters is being rapidly developed (See, e.g., W. J. Treat and W. A. Aldred, "An Inexpensive Chamber for Selecting and Maintaining Phototrophic Plant Cells," Biotech. Techniques 4, 91 (1989)). The availability of an abundant, relatively inexpensive source of cells suggests that these might be useful for removal of certain compounds from large volumes of complex effluent solutions. The ability to use dead, dehydrated cells may also provide a means of treating waste directly.

Reference will now be made in detail to the present preferred embodiments of the invention, examples of which are illustrated in the accompanying drawings.

A. Preparation and maintenance of plant suspension cultures. Suspension cultures of D. innoxia were maintained in the dark at 30° C. as 50 or 100 ml batch suspension cultures as has previously described in Paul J. Jackson, E. Jill Roth, Peter McClure, and Cleo M. Naranjo, "Selection, Isolation, and Characterization of Cadmium-Resistant Datura innoxia Suspension Cultures," Plant Physiol. 75, 914 (1984). Flask volume was maintained at a flask volume to culture volume of 5 to 1 in order to permit adequate oxygenation of the cells through aeration. Cells were grown in modified Gamborg's 1B5 medium supplemented with vitamins. Under these conditions, cell number doubles approximately every 24 hours.

B. Measurement of plant cell growth and division. Plant cell number was measured indirectly by determining the change in packed cell volume of the culture. Five ml of cell culture was centrifuged for 1 minute at 200 g and the volume of packed cells determined.

C. Conversion of cells to protoplasts. An equal volume of cells was mixed with protoplasting solution (600 mM KNO₃, 3 mM CaCl₂, 1 mM KH₂ PO₄, pH adjusted to 5.5 with KOH) containing 0.5% (w/v) Cellulysin (CalBiochem, LaJolla, Calif.) and 0.05% pectlyase (Sigma Chemical Co., St. Louis, Mo.). The suspension was incubated at 30° C. for one hour with gentle shaking. Protoplasts were removed from the remaining cells by filtration through a 45 micron nylon sieve.

D. Measurements of barium uptake. Barium uptake was measured from the cell culture medium and from waste solutions. A similar method was employed for plutonium. Measurement of removal of barium from media followed addition of known concentrations of Ba(NO₃)₂ and radioactive ¹³³ Ba²⁺. Removal of Ba²⁺ was measured as a decrease of radioactivity present in the medium from which cells were removed. This was confirmed by measurement of an increase of radioactivity in the cells removed from the medium. In all experiments, the amount of radioactivity associated with the cells was within 10% of the amount of radioactivity removed from the medium. Measurement of radioactivity was by scintillation spectrophotometry following addition of aqueous scintillation cocktail (Formula 963, Dupont New England Nuclear, Boston, Mass.) to samples.

E. Fractionation of cell components. Cells were collected from media by centrifugation for 1 minute at 200 g and washed twice in ice cold buffer containing 10 mM Tris-HCl, pH 7.4, 10 mM KCl and 1.5 mM MgCl₂. Pellets were resuspended in one-half the original culture volume of the same buffer containing 20 mM 2-mercaptoethanol and homogenized in an Elvehjem tissue grinder. The homogenate was then centrifuged at 12,000 g for 15 minutes and the supernatant collected. Measurement of radioactive ¹³³ Ba was accomplished by measuring radioactivity in the total extract, then in the supernatant following centrifugation to remove insoluble components. Radioactivity in the pellet was confirmed by resuspension of the pellet in the above buffer and assaying a known volume of this suspension for radioactivity.

F. Measurements of cell dry weights and preparation of dehydrated cells. Cells were collected from growth medium by centrifugation for 1 minute at 200 g, washed once in fresh growth media and collected again by centrifugation. Cell pellets were resuspended in a solution containing 70% ethanol (v/v) 30% distilled water. Slurries of cells were poured into preweighed weigh boats and placed at 42° C. in a drying oven. Cells were considered completely dehydrated when no further change in weight with additional heating could be detected.

Having generally described the invention and the experimental procedures utilized in the verification of its operation, the specific embodiments thereof are demonstrated in the following examples.

EXAMPLE I Barium Removal

Barium is toxic to most living species. However, D. innoxia plant cell suspension cultures can grow in the presence of concentrations of this metal ion which are significantly higher than those which are toxic to mammals. Tolerance to high concentrations of Ba²⁺ suggests that the cells have some mechanism of either excluding barium, or sequestering it in a nontoxic or less toxic form. Approximately 1 pmole of Ba²⁺ can be bound to every cell. This suggests that the metal-binding component is either very abundant or can bind large amounts of Ba²⁺. Greater than 5% of the dry weight of cells grown in high concentrations of Ba(NO₃)₂ is Ba²⁺.

A. Growth of D. innoxia cells in different concentrations of Ba²⁺. In order to determine what concentrations of Ba²⁺ are toxic to cell suspension cultures of D. innoxia, exponentially growing cells were exposed to different concentrations of this ion. Turning now to the figures, FIG. 1 illustrates the growth of D. innoxia cells in different concentrations of Ba²⁺ for different periods. Rapidly growing D. innoxia cell suspension cultures were transferred to fresh media containing 0, 100, 250, 500 and 1000 μM Ba(NO₃)₂. Measurements of cell growth were determined by measuring the packed cell volume (PCV) of 5 ml of culture at different times after addition of Ba²⁺. Cells were transferred to fresh media containing the original concentration of Ba²⁺ every 48 hours to maintain rapid cell division. Clearly, there is no significant difference in the doubling time and cell volume of cells growing in any concentration of Ba²⁺ up to 2 mM. Above this concentration, the metal ion was found to precipitate from solution. However, if cells are grown in media containing precipitated Ba²⁺, the precipitate vanishes after two days, suggesting that removal of the soluble ion by the cells shifts the equilibrium resulting in the solubilization of the precipitated barium. Growth of cells for extended periods in 1 or 2 mM Ba(NO₃)₂ does not inhibit cell growth and division. Cultures growing in these concentrations for over 350 generations show no change in cell doubling times when compared to the same cells growing in the absence of this Ba²⁺.

B. Removal of Ba²⁺ from cell growth medium. In order to measure uptake of Ba²⁺ into cells, cultures containing 2×10⁶ cells/ml and growing in media containing no additional barium were transferred to media containing different concentrations of Ba(NO₃)₂ +0.1 μCi/ml carrier-free ¹³³ Ba(NO₃)₂ and allowed to grow for 24 hours. During this period, the cell number approximately doubles. Cells were then collected from the medium by centrifugation, washed twice and homogenized. The medium, total homogenate and supernatant following removal of insoluble material were then assayed for radioactivity. FIG. 2 shows the distribution of Ba²⁺ among the different fractions after removal by the growing D. innoxia cells. Values are plotted against the total amount of Ba(NO₃)₂ initially present in the media.

FIG. 2a shows the barium bound to the cells, FIG. 2b that barium bound to the insoluble component, and FIG. 2c barium remaining in the medium. Almost 90% of the Ba²⁺ ion is associated with the cells following growth in 1 mM Ba²⁺. Virtually all of the metal ion associated with the cells is bound to a component of the insoluble cell homogenate. These results suggest that the cells are able to sequester large amounts of Ba²⁺. They also suggest that either the metal binding is rather weak or the number of potential binding sites is close to saturation when cells have been grown in 1 mM Ba²⁺. The fact that this concentration of barium does not appear to be toxic to the cells suggests that the latter is probably correct. A very large portion of Ba²⁺ is removed by the cells in media containing up to 500 μM Ba²⁺. Above this concentration, significant amounts of Ba²⁺ remain in the media. Removal of cells containing Ba²⁺ followed by addition of new cells results in the decrease of the barium ion in solution to about the same percentage of removal. Successive treatments result in the barium ion falling to below the detectable limit of 1 ppb. This behavior suggests a saturation of all of the Ba-binding sites within the first set of cells. The results demonstrate a tight binding of Ba²⁺ to an insoluble fraction of the cells.

C. Identification of the cellular component binding Ba²⁺. Measurements of the rate of uptake of Ba²⁺ are shown in FIG. 3. D. innoxia cells were placed into media containing 1 mM Ba(NO₃)₂ plus carrier-free ¹³³ Ba for different periods of time. Cells were then removed from the media by centrifugation and the media and cell homogenate assayed for ¹³³ Ba activity. The results demonstrate an almost immediate interaction of soluble Ba²⁺ with some component of the cells. The rapid nature of this interaction suggests that the metal ion is not passing through cellular membranes. The data therefore strongly suggest that the Ba²⁺ is binding to some external component of the cells, perhaps a component of the cell wall or membrane. D. innoxia cells growing in the absence of Ba²⁺ were transferred to media containing 500 μM Ba(NO₃)₂ plus 0.2 μCi/ml ¹³³ Ba²⁺ and grown an additional 24 hours. Cells were then converted to protoplasts. Within two hours, 95% of the cell population was converted as the walls were digested. At different times following exposure to the enzymes, samples were collected, filtered through 45 micron screens, washed protoplasts were collected from suspension by centrifugation for 3 minutes at 200 g, and the total amount of barium assayed. Protoplasts will pass through such a sieve, while cells and cell clumps cannot. Measurement of the total amount of barium found in the cells and protoplasts demonstrated a loss of Ba²⁺ -binding by protoplasts. Please refer to Table 1. Data presented are from four independent experiments. The remaining 5% of the cells bound over two-thirds of the Ba²⁺ present. These results suggest that some component of the cell wall is involved in Ba²⁺ -binding. Addition of purified cellulose to media containing Ba²⁺, however, did not result in the rapid removal of this ion from solution (data not shown) suggesting that some other factor within the wall is responsible for metal-binding.

                  TABLE 1                                                          ______________________________________                                         Association of Ba.sup.2+  with plant cells and plant                           protoplasts.                                                                           % of total Ba.sup.2+  associated with                                  Exp. No.  Cells       Media   Protoplasts                                      ______________________________________                                         1         68.7        24.2    7.1                                              2         71.6        21.5    6.9                                              3         63.6        20.6    15.8                                             4         68.7        26.8    4.5                                              ______________________________________                                    

D. Stability of Ba-binding. In order to further characterize the binding component(s) and to determine the stability of metal-binding under different conditions, the effect of pH on metal binding was determined. Ten ml samples of cells grown in 1 mM Ba²⁺ plus 0.1 μCi/ml carrier-free ¹³³ Ba for 24 hours were collected and extracted after being washed twice with media containing no additional Ba²⁺, and each extract was adjusted to a different pH. Samples were then incubated overnight at 22° C. The resulting samples were centrifuged to separate the aqueous from the insoluble phases, and the supernatant was assayed for ¹³³ Ba content. FIG. 4 demonstrates that metal binding is quite stable over a pH range from 1 to 10. These results suggest that binding is quite complex, since ionic binding to a single, simple entity would result in the loss of affinity of the binding site for the metal ion upon a change in pH around the pKa of such a specific site.

Extractions containing different concentrations of Na⁺ were found to demonstrate relative stability to different salt concentrations. However, at higher concentrations, Ba-binding is lost. This demonstrates that the interaction between this metal ion and the cellular component is ionic in nature. This is illustrated in FIG. 5, which shows the binding of barium by cell components at different Na+ concentrations. D. innoxia cells were grown to 4×10⁶ cells per ml, then transferred to solutions containing 500 μM Ba(NO₃)₂, 0.1 μCi/ml carrier-free ¹³³ Ba and different concentrations of NaCl. Suspensions were mixed for 24 hours, then separated by centrifugation. Cell pellets were washed in buffer containing the same concentration of Na+ ion, then extracted.

E. Removal of Ba²⁺ from complex waste solutions. If plant cells are to offer an alternative to current technology for the removal of Ba²⁺ solutions, binding of this ion by cells under the conditions found within such solutions must be demonstrated. Samples of such waste were therefore obtained and assays of Ba²⁺ and other components performed. The amount of Ba²⁺ bound by the cells varied according to the original amount present in the waste sample tested. The "percent dry weight"=weight of bound Ba²⁺ divided by the total weight of the cells and Ba²⁺. Two-day old suspension cultures of D. innoxia (8×10⁶ cells/ml) were collected by centrifugation. One-half of the cells were washed twice with 70% ethanol, then dehydrated by heating at 42° C. Living cells and dehydrated samples were then resuspended in 50 ml of filter-sterilized waste solution containing known amounts Ba(NO₃)₂ plus of 0.1 μCi/ml carrier-free ¹³³ Ba*. Suspensions were incubated with shaking at 22° C. overnight, then collected from the waste by centrifugation. The amount of barium attached to the cells and left in the waste was measured. The amount of barium found in the different fractions of an extract of the living cells was also determined. Table 2 demonstrates the removal of radioactive Ba²⁺ from waste solutions. This information was confirmed by an independent assay of Ba²⁺ within the samples (data not shown). Addition of dead, dehydrated cells to waste also resulted in removal of Ba²⁺ from solution. Measurement of radioactivity and dry weights following removal of Ba²⁺ from solution demonstrated that as much as 5.3% of the dry weight of the cells is barium following exposure to waste containing this metal ion.

                  TABLE 2                                                          ______________________________________                                         Removal of Ba.sup.2+  from waste solutions by living and                       dehydrated plant suspension culture cells.                                                 Living Cells                                                                             Dehydrated Cells                                         ______________________________________                                         Associated with                                                                              93.75 (± 5.25)                                                                          96.10 (± 5.86)                                    cells (%):                                                                     Ba.sup.2+  remaining                                                                          6.25 (± 0.35)                                                                           5.9 (± 0.36)                                     in waste solution                                                              (%):                                                                           Insoluble     90.10 (± 2.47)                                                                          not measured                                         portion of cell                                                                extract:                                                                       Soluble portion                                                                               2.65 (± 0.07)                                                                          not measured                                         of cell extract:                                                               Percent dry   not measured                                                                               2.8-5.3*                                             weight:                                                                        ______________________________________                                    

EXAMPLE II Plutonium Removal

The experiment for binding Pu is very similar to that for binding Ba. The major difference is that Pu(IV) is readily hydrolyzed to give polymeric material at acid concentrations below 0.1N and therefore complexing agents are needed in the aqueous solution to maintain the Pu(IV) in soluble form in the pH 1-10 range. A wide range of pH representative of environmental conditions and some process waste streams as well as the competitive binding of the Pu(IV) by the very strong chelators citrate and EDTA were examined. The test solutions were "spiked" with a small amount of Pu(IV) in HCl to give the solutions shown in Table 3. A volume of packed cells (2-3 ml) was suspended in each solution and the plutonium concentration in the supernatant monitored by scintillation spectrometry after removing the cells by centrifugation. Control solutions

                                      TABLE 3                                      __________________________________________________________________________                      Initial Pu                                                                          Final Pu                                                                            % Pu Cell Dry                                       Solution*  Equil. pH                                                                            CPM  CPM  removed                                                                             Weight (mg)                                    __________________________________________________________________________     J-13 water 5.5   3989  624 84   30.1                                           control    3.5   3968 4064                                                     0.1 N HCl  1.0   4296  796 81   25.7                                           control    1.0   4268 4338                                                     0.01 M sodium                                                                             5.3   4242 2642 38   27.9                                           citrate control                                                                           5.9   4188 4190                                                     0.1 M Na bicarbonate                                                                      8.0   4100  634 85   19.7                                           control    8.0   4276 4110                                                     0.1 M Na EDTA                                                                             10.0  4136 3208 22   41.4                                           control    10.0  4052 4308                                                     0.01 M Ba(NO.sub.3).sub.2                                                                 5.6   4324  493 89   30.4                                           control    3.5   4198 3777                                                     J-13 water 1.1   5764 1206 79   32.6                                           0.1 N HCl  0.5   5371  911 83   35.4                                           0.1 M Na bicarbonate                                                                      7.5   5438 2384 56   20.9                                           0.1 M Na citrate                                                                          1.3   5591  931 83   33.2                                           __________________________________________________________________________

without added cells were used to verify that the Pu(IV) did not form a polymeric species that could be removed from solution by the centrifugation step.

The D. innoxia cells (nonviable in these solutions) removed 80-90% of the Pu activity from solution over a wide range (1-8) of pH values. The extent of Pu removal could be higher since some of the α activity is due to americium contained in the original plutonium oxide. Citrate and EDTA, which form very strong complexes with Pu(IV), were found to significantly reduce Pu uptake by the plant cell material. A large excess of Ba did not significantly interfere with Pu uptake. Measurements of the Pu concentration taken after one hour of contact show that the solutions near pH 1 are essentially at equilibrium in this time period, whereas the solutions at higher pH require several hours to reach equilibrium. The longer equilibrium times at higher pH are probably the result of slower ligand exchange kinetics caused by the more strongly complexing ligands needed to keep the Pu(IV) in solution.

Solutions 1-6 (10 ml) were spiked with 50 μ1 of a solution of 10⁻⁴ M Pu(IV) in 1N HCl and "final" Pu counts were obtained after 75 hours of shaking with the cellular material. Solutions 7-10 (10 ml) were spiked with 100 μl of 10⁻⁴ M Pu(IV) in 12N HCl and "final" Pu counts were obtained after 24 hours of shaking with the cellular material. The beginning Pu(IV) concentration was therefore 5×10⁻⁷ =500 nM for the former solutions and 1 μM for the latter solutions.

EXAMPLE III Iron Removal

Cells were incubated in 0.19 μM ⁵⁹ Fe (15 μCi) for 24 hours, after which they were harvested by centrifugation from the growing medium, washed twice in a solution containing 10 mM Tris-HCl, pH 7.4, 10 mM MgCl₂, 1.5 mM KCl, and 50 mM 2-mercaptoethanol, resuspended in the same solution, and homogenized. It was found that 77.8% of the total Fe²⁺ from the medium containing the iron was sequestered by the cells, with 14.4% found in the soluble fraction of the cell homogenate, and 85.6% in the insoluble components, most likely the cell wall.

EXAMPLE IV Explosive Removal

FIG. 6 shows three high pressure liquid chromatography traces (Retention Time (minutes) v. Optical Density at 254 nm) of aqueous solutions containing explosive compounds and some by-products thereof. FIG. 6a is the trace of a typical waste solution containing several explosives and associated compositions. Present are quantities of DNB (dinitrobenzene) or TNB (trinitrobenzene), TNT, RDX, and HMX. FIG. 6b is a chromatographic trace of the solution shown in FIG. 6a after treatment with D. innoxia for four hours. FIG. 6c is a chromatographic trace of the soluble portion of an extract from the D. innoxia cells used to treat the solution characterized in FIG. 6a. The cell extract was mixed (1:1) with a buffer containing acetonitrile, in which the explosive molecules are very soluble. The large peak with the short retention time in FIG. 6b is the result of sucrose in the plant cell medium. The large peak with essentially the same retention time in FIG. 6c is the result of sucrose and other unidentified material released from the cells during the extraction process. HMX has the same retention time as sucrose. However, independent experiments have demonstrated that at least some of the HMX is removed from solution.

The foregoing description of several preferred embodiments of the invention have been presented for purposes of illustration and description. It is not intended to be exhaustive or to limit the invention to the precise form disclosed, and obviously many modifications and variations are possible in light of the above teaching.

The embodiments were chosen and described in order to best explain the principles of the invention and its practical application to thereby enable others skilled in the art to best utilize the invention in various embodiments and with various modifications as are suited to the particular use contemplated. It is intended that the scope of the invention be defined by the claims appended hereto. 

What is claimed is:
 1. A method for reducing the concentration of metal ions in aqueous solution comprising the steps of adding a suspension of plant cells selected from the group consisting of Citrus citrus, Black Mexican sweet corn and D. innoxia to the aqueous solution, and separating the plant cells from the solution after sufficient interaction time for the metal ions to interact with the plant cells has taken place.
 2. The method as described in claim 1, further comprising the step of dehydrating the plant cells before said step of addition to the aqueous solution.
 3. A method for reducing the concentration of Ba²⁺ in aqueous solution comprising the steps of adding a suspension of plant cells selected from the group consisting of Citrus citrus, Black Mexican sweet corn and D. innoxia to the aqueous solution, and separating the plant cells from the solution after sufficient interaction time for the Ba²⁺ to interact with the plant cells has taken place.
 4. The method as described in claim 3, further comprising the step of dehydrating the plant cells before said step of addition to the aqueous solution.
 5. A method for reducing the concentration of plutonium ions in aqueous solution comprising the steps of adding a suspension of plant cells selected from the group consisting of Citrus citrus, Black Mexican sweet corn and D. innoxia to the aqueous solution, and separating the plant cells from the solution after sufficient interaction time for the plutonium ions to interact with the plant cells has taken place.
 6. The method as described in claim 5, further comprising the step of dehydrating the plant cells before said step of addition to the aqueous solution.
 7. A method for reducing the concentration of Fe²⁺ in aqueous solution comprising the steps of adding a suspension of plant cells selected from the group consisting of Citrus citrus, Black Mexican sweet corn and D. innoxia to the aqueous solution, and separating the plant cells from the solution after sufficient interaction time for the Fe²⁺ to interact with the plant cells has taken place.
 8. The method as described in claim 7, further comprising the step of dehydrating the plant cells before said step of addition to the aqueous solution. 